Removal of thermal stable salts from organic solvents

ABSTRACT

A Method for removing salts, which cannot be thermally regenerated in a temperature range from 0°-200° C., from organic solvents in aqueous solution by evaporation, wherein the normal boiling point of the organic solvents is higher than water. The organic components contained in the solvent and the salt-like components which are contained in the organic components are enriched by evaporating water and a portion of the organic components in a liquid phase which is formed in a first container. The salt-like components are concentrated in the liquid phase which is forming in the second container, and a partial stream of the liquid phase which is formed in the second container is discharged from the second container.

The technical field of the present invention relates to a process for removal of salts thermally non-regenerable in a temperature range from 0° C. to 200° C. from organic solvents, such as aqueous amine solutions, by evaporation. The inventive process is to support a process for the removal of acid gas constituents, such as CO₂ and H₂S, and reprocesses a partial stream of the solvent main stream containing the thermally non-regenerable salts. The thermally non-regenerable salts are formed, for example, by the feed of traces of strongly acidic gases, such as Cl₂, HCOOH, SO₂, SO₃, NO₂, etc. together with the input gas supplied to the absorber of the scrubber.

Regeneration of a chemical detergent is achieved by the fact that constituents such as acid gas constituents, e.g. CO₂, H₂S, HCN, mercaptans, etc. chemically bound in an absorption are thermally reconverted at elevated temperatures into their initial constituents without this causing an alteration of the chemical detergent in its chemical structure. Thus it represents a reversible chemical process that can be influenced by a change in temperature.

This principle can be applied in particular to light-volatile, relatively weakly acidic constituents as outlined hereinabove by way of examples. Aqueous amine solutions, e.g. MEA, DEA, TEA, DGA, DIPA, MDEA or solvents utilized in the Flexsorb process which is known to an expert are very often applied as detergents/solvents for such constituents. Thus, thermally regenerable salts are formed, the detergent/solvent being recoverable in a temperature range from 0° C. to 200° C. and the absorbed gases in the regeneration column being again removed from the solution.

Amine constituents are also utilized as additives in what are called hybrid detergents/solvents, which an expert in general understands to be a combination of physical and chemical detergents, e.g. sulfinol.

If only light-volatile, weakly acidic constituents are available in a given gas stream, one of these afore-mentioned detergents/solvents can be utilized very advantageously for the removal of these acid gas constituents. Such a process is, for example, described in DE 3408851 A1. Here, the removal of CO₂ and/or H₂ 5 from gases by means of an aqueous absorption liquid containing methyl diethanol amine is described. Accordingly, the burdened absorption liquid is expanded in at least two expansion stages for regeneration. A gas containing CO₂ and/or H₂S is withdrawn at the heads and the absorption liquid is enriched at the bottom and then passed into a second tank. The bottom of the final expansion stage contains the regenerated absorption liquid.

In most applications, however, more strongly acidic constituents such as chlorides, SO_(x) constituents, sulfates, thiosulfates, thiocyanates, organic acids, such as formiates, acetates, etc. entrained by the gas stream also get into the solvent. These more strongly acidic constituents cannot be removed from the solvent by implementing the thermal measures outlined hereinabove and described by way of example in DE 3408851 A1, so that these salt-like constituents termed heat stable salts, and hereinafter also termed HSS, are continually enriched. Hence, this concerns salts thermally non-regenerable in a temperature range from 0° C. to 200° C.

For two different reasons, this enrichment is extremely disadvantageous for the scrubbing process:

On the one hand, due to the chemical bond of these constituents with the active scrubbing constituent, e.g. amine, the active scrubbing capacity for acid gas constituents is (at least) proportionally reduced. On the other hand, a rising concentration of HSS constituents leads to a strongly increasing corrosiveness of the scrubbing solution. As a rule, the HSS content for a still tolerable corrosiveness of the solution should not exceed 3% by wt.

On account of these reasons, entrained HSS constituents must be removed and/or sluiced out from the solvent. The simplest, though most expensive possibility is discharging such an amount of solvent that corresponds to the amount of HSS constituents carried in. This procedure is generally termed “repulsive mode”. In most cases, however, considerably more solvent gets lost than is sluiced out as HSS. For example, this occurs if the HSS concentration amounts to 3% by wt. and the amine concentration, for instance, amounts to 40% by wt.

According to prior art in technology, a host of different processes is available to selectively remove HSS constituents from the process, e.g. distillative processes and ion exchanger processes, too. Such a process treatment stage is also termed reclaimer or reclaimer unit. One of those processes operating in the most selective manner is the ion exchanger process. However, relatively large amounts of wastewaters are produced there due to scrubbing and flushing processes.

A semi-continuously working evaporator, too, is frequently applied. Such an evaporator operates by feeding a partial stream of the solvent burdened with HSS and withdrawn from the main solution circulation to an evaporator, the chemically reacting detergent constituent, e.g. MEA from an aqueous MEA solution, supplied to the evaporator being exactly evaporated in the same extent as it is supplied to the evaporator. Obtained here is an amine concentration of e.g. 80% by wt. MEA in the solution. This is the case because under these process conditions the MEA quantity existing in the input stream precisely exists in the gas phase.

Had there been no HSS constituents and no other high-boiling constituents in the solvent input stream, the process could be continued for an arbitrarily long period of time. On account of the HSS constituents existing in the input solution, however, an enrichment of these salt-like constituents occurs in the evaporator.

When a concentration of e.g. 10% by wt. of a salt freight in the evaporator is achieved, the process in the evaporator is reversed from a continuous mode to a discontinuous mode. By addition of a strong base, e.g. NaOH, the HSS constituents chemically bound to amine are bound to the Na⁺ ion so that the amine hitherto fixed to HSS can also be evaporated. By addition of water vapour and an external heating, the amine solution now existing in the evaporator is evaporated until almost no amine can be detected any more in the gas phase (e.g.<0.1% by vol.).

If this point is reached, the whole charge existing in the evaporator is drained from the evaporator and must be disposed of. However, there still exists a residual concentration of 20 to 30% by wt. of amine in the liquid phase.

If one compares the application of this reclaimer type with the simple repulsive mode outlined hereinabove, it results a reduction of the amine loss by factor 3 to 4 as compared with the repulsive mode, which would correspond to a reclaimer efficiency degree of 66 to 75% relative to a mere repulsive mode. But the loss of expensive solvent (2 to 10

per kg) still is quite high. However, in terms of capital investment costs and consumption of utilities, the evaporator reclaimer described above is very cost-efficient as compared with an ion exchanger, even though two evaporators of this kind are generally implemented to ensure permanent reclaimer operation. This is the case, in particular, if the reclaimer steam evolving on evaporation is passed into the sump of an amine regenerator where it can be exploited as stripping steam for thermal stripping of amine from acid gas constituents, thus reducing the external amount of heat required for amine regeneration. Had there not been the residual losses of amine, the evaporator concept described above would be the ideal reclaimer concept for chemically reacting organic solvents in aqueous solution.

A process making it possible to maintain the advantages outlined hereinabove while simultaneously reducing the losses of solvent would therefore be absolutely advantageous. Providing such a process is the task pursued by the present invention.

The inventive task is solved by a process for removal of salts thermally non-regenerable in a temperature range from 0° C. to 200° C., from organic solvents in an aqueous solution by evaporation, the normal boiling point of organic solvents being higher than that of water, and by enriching the organic constituents existing in the solvent as well as the salt-like constituents existing therein in a liquid phase forming by evaporation of water and a portion of the organic constituents of a first tank, and discharging an evolving vaporous phase from the first tank. In particular, the liquid phase formed in the first tank is passed into a second tank, water in vaporous and/or liquid form being passed into the second tank, water and another portion of the organic constituents contained in the solvent being evaporated and forming a vaporous phase which is discharged from the second tank, said salt-like constituents being enriched in concentration in the liquid phase forming in the second tank, and wherein a partial stream of the liquid phase formed in the second tank is discharged from the second tank.

The term “tank” as used in this description should be understood to mean all commonly known devices that can be utilized for evaporation processes.

The temperature at which evaporation is operated, among other factors, depends on the normal boiling point of the organic solvent to be recovered by means of the inventive process. Determination and stipulating such parameters are well known to an expert in this field and should be considered as a standard in prior art technology.

In a preferred embodiment of the present invention, the salt concentration of the liquid phase formed in the first tank is determined, and the liquid phase of the first tank is passed into the second tank as soon as the concentration of salt-like constituents of the liquid phase to be carried over has reached a maximally admissible concentration at which the salt-like constituents are still soluble in the liquid phase. In particular, the liquid phase of the first tank is passed into the second tank as soon as a concentration of the salt-like constituent in the liquid phase of 5 to 35% by wt., preferably 5 to 25% by wt., and more particularly preferably 5 to 15% by wt., and most preferably 8 to 12% by wt., is achieved.

In a further configuration of the present invention, the salt concentration of the liquid phase formed in the second tank is determined and a partial stream of the liquid phase from the second tank is discharged as soon as the concentration of salt-like constituents of the liquid phase to be discharged has reached a maximally admissible concentration at which the salt-like constituents are still soluble in the liquid phase. In particular, a partial stream of the liquid phase is discharged from the second tank as soon as a concentration of the salt-like constituent in the liquid phase of 25 to 65% by wt., preferably 40 to 65% by wt., and more particularly preferably 45 to 65% by wt., and most preferably 55 to 65% by wt., is achieved.

The first tank and/or the second tank is optionally heated and/or cooled in order to ensure appropriate evaporation.

It is advantageous to provide water in the second tank already before the liquid phase formed in the first tank is carried over into the second tank. The water to be provided here preferably is boiler feed water originating from other units of an industrial plant and further used at this location. The second tank is filled only partly with water. The height of the water level influences the time until the correspondingly defined limit concentration of salt-like constituents in the liquid phase formed by evaporation is reached in the second tank so that the liquid phase is discharged from the second tank. The optimal height of the water level will be determined by an expert in this field through routine tests as the case may be.

With the inventive process, it is of advantage to merely produce a concentrated salt solution depleted in organic constituents as wastewater that encompasses the liquid phase formed in the second tank.

In another embodiment of the present invention, merely a partial stream of a main circulating stream of an industrial plant encompassing an organic solvent burdened with thermally stable salts is supplied to the first tank. Furthermore, the vaporous phases of the first and/or second tank formed by evaporation are returned into a main circulating stream of an industrial plant. To this effect, a prior condensation of these vaporous phases is advantageous. Non-condensable gases are sluiced out and sluiced in, if any, into the process upstream to an absorber arranged in the relevant industrial plant. These vaporous phases generated with the inventive process can alternatively be returned into a stripper sump.

In a further embodiment of the present invention, claim is laid to the continuously operating mode of the process. Accordingly, the liquid phase formed in the first tank is continuously passed into the second tank, and water in vaporous and/or liquid form is continuously passed into the second tank, and by way of a controlled supply or discharge of heat, water and portions of the organic constituents contained in the solvent are continuously evaporated, thus forming a vaporous phase which is discharged from the second tank, said salt-like constituents being enriched in concentration in the liquid phase forming in the second tank, and a partial stream of the liquid phase formed in the second tank is continuously discharged from the second tank and forms a wastewater stream which encompasses a concentrated salt solution depleted in organic constituents, and the vaporous phases of the first and/or second tank which are formed by evaporation are returned into a main process stream of an industrial plant.

It is advantageous to feed a strong base, such as NaOH, to the first tank and/or the second tank.

Furthermore, distillative intermediate stages which can be integrated into the process at any location to ensure a further clean-up of the resulting process streams are optionally conceivable.

It is of advantage to initially run the process in a semi-continuous manner during start-up so that an enrichment of the salt-laden constituents in the liquid phase of the second tank is achieved by operating initially only the first tank continuously after a certain concentration of salt-laden constituents has been achieved in the liquid phase forming there, and reversing to a completely continuous mode only after having achieved a corresponding concentration of salt-laden constituents in the liquid phase of the second tank by discharging a partial stream of the liquid phase then continuously from the second tank.

Applying this mode of operation makes it possible to reduce amine losses down to a minimum. By means of this process, it is possible to achieve reclaimer efficiency degrees of more than 99%.

Considering a 800 MW coal-fired power plant, savings accounting for approx. 25 million

per year result mathematically as compared to an operating mode of a conventional prior art evaporator reclaimer.

By means of the inventive process mode, it is also possible to perform a removal of CO₂ and/or H₂S and/or HCN and/or mercaptans from flue gases without the need for an additional NaOH scrubbing prior to the actual amine scrubbing for residual removal of SO_(x) from flue gas. This scrubbing is, for example, operated according to the process described in DE 3408851 A1. This conventional acid gas scrubbing is then followed by the scrubbing according to the inventive process. This is to be considered as an advantageous application of the inventive process in an industrial plant. This is feasible because amine losses are reduced to a sufficiently low level by implementing the inventive reclaimer operating mode. 

1. A process for removal of salts thermally non-regenerable in a temperature range from 0° C. to 200° C. from organic solvents in an aqueous solution by evaporation, the normal boiling point of organic solvents being higher than that of water, and by enriching the organic constituents existing in the solvent as well as the salt-like constituents existing therein in a liquid phase forming by evaporation of water and a portion of the organic constituents of a first tank, and discharging an evolving vaporous phase from the first tank, wherein the liquid phase formed in the first tank is passed into a second tank, water in vaporous and/or liquid form being passed into the second tank, water and another portion of the organic constituents contained in the solvent being evaporated and forming a vaporous phase which is discharged from the second tank, said salt-like constituents being enriched in concentration in the liquid phase forming in the second tank, and wherein a partial stream of the liquid phase formed in the second tank is discharged from the second tank.
 2. The process according to claim 1, wherein the salt concentration of the liquid phase formed in the first tank is determined, and in that the liquid phase of the first tank is passed into the second tank as soon as the concentration of salt-like constituents of the liquid phase to be carried over has reached a maximally admissible concentration at which the salt-like constituents are still soluble in the liquid phase.
 3. The process according to claim 2, characterized in that wherein the liquid phase of the first tank is passed into the second tank as soon as a concentration of the salt-like constituent in the liquid phase of 5 to 35% by wt., preferably 5 to 25% by wt., and more particularly preferably 5 to 15% by wt., and most preferably 8 to 12% by wt., is achieved.
 4. The process according to claim 1, wherein the salt concentration of the liquid phase formed in the second tank is determined, and a partial stream of the liquid phase is discharged from the second tank as soon as the concentration of salt-like constituents of the liquid phase to be discharged has reached a maximally admissible concentration at which the salt-like constituents are still soluble in the liquid phase.
 5. The process according to claim 4, wherein a partial stream of the liquid phase is discharged from the second tank as soon as a concentration of the salt-like constituent in the liquid phase of 25 to 65% by wt., preferably 40 to 65% by wt., and more particularly preferably 45 to 65% by wt., and most preferably 55 to 65% by wt., is achieved.
 6. The process according to claim 1, wherein the first tank and/or the second tank is externally heated and/or cooled.
 7. The process according to claim 1, wherein water is provided in the second tank already before the liquid phase formed in the first tank is carried over into the second tank.
 8. The process according to claim 1, wherein merely a concentrated salt solution depleted in organic constituents is produced as wastewater that encompasses the liquid phase formed in the second tank.
 9. The process according to claim 1, wherein merely a partial stream of a main circulating stream of an industrial plant encompassing an organic solvent burdened with thermally stable salts is supplied to the first tank.
 10. The process according to claim 1, wherein the vaporous phases of the first and/or second tank formed by evaporation are returned into a main circulating stream of an industrial plant.
 11. The process according to claim 1, wherein the liquid phase formed in the first tank is continuously passed on to the second tank, and water in vaporous and/or liquid form is continuously passed into the second tank, and in that by way of a controlled supply or discharge of heat, water and portions of the organic constituents contained in the solvent are continuously evaporated, thus forming a vaporous phase which is discharged from the second tank, said salt-like constituents being enriched in concentration in the liquid phase forming in the second tank, and wherein a partial stream of the liquid phase formed in the second tank is continuously discharged from the second tank and forms a wastewater stream which encompasses a concentrated salt solution depleted in organic constituents, and wherein the vaporous phases of the first and/or second tank which are formed by evaporation are returned into a main process stream of an industrial plant.
 12. The process according to claim 1, wherein a strong base is supplied to the first tank and/or the second tank.
 13. The process according to claim 1, wherein first a removal of CO₂ and/or H₂S and/or HCN and/or mercaptans from flue gases is carried out. 